Huazheng HZJY880 Operating instructions

Type
Operating instructions

Huazheng HZJY880 Computer BOD5 Measator is a reliable instrument for measuring Biochemical Oxygen Demand (BOD5), a crucial indicator of water quality. With its advanced features, it offers precise and efficient BOD5 determination for various applications. Here are some of its capabilities:

  • Accurate Measurement: Provides accurate BOD5 values comparable to the chemical dilution method, ensuring reliable results.

  • Real-Time Monitoring: Continuously monitors BOD5 levels throughout the incubation period, allowing for real-time observation of the biochemical reaction curve.

  • Wide Measurement Range: Covers a wide measurement range of 0 to 1000 mg/L, accommodating diverse water samples. For values exceeding this range, simple dilution is recommended.

Huazheng HZJY880 Computer BOD5 Measator is a reliable instrument for measuring Biochemical Oxygen Demand (BOD5), a crucial indicator of water quality. With its advanced features, it offers precise and efficient BOD5 determination for various applications. Here are some of its capabilities:

  • Accurate Measurement: Provides accurate BOD5 values comparable to the chemical dilution method, ensuring reliable results.

  • Real-Time Monitoring: Continuously monitors BOD5 levels throughout the incubation period, allowing for real-time observation of the biochemical reaction curve.

  • Wide Measurement Range: Covers a wide measurement range of 0 to 1000 mg/L, accommodating diverse water samples. For values exceeding this range, simple dilution is recommended.

HZJY880
Computer BOD5 Measator
Huazheng Electric Manufacturing (Baoding) Co., Ltd
Contents
I. Introduction to the instrument and its scope of use ...................................................1
II. Working principle ....................................................................................................... 1
III. Main technical indicators ..........................................................................................2
IV. Installation and use .................................................................................................. 3
V. Analysis method and analysis steps ......................................................................... 4
VI. Normal maintenance and troubleshooting of common faults ............................... 16
VII. Precautions ........................................................................................................... 19
VIII. BOD5 Tester Packing List ....................................................................................21
1
I. Introduction to the instrument and its scope of use
Biochemical oxygen demand (BOD5) is a must-measured item for water quality evaluation
and an important quality indicator for measuring the pollution of water by organic matter.
880 type microcomputer BOD5 measuring instrument is a new type of instrument for BOD
measurement by air pressure difference method, which is processed by microcomputer and
liquid crystal display. It can accurately provide measurement results comparable to chemical
dilution method, directly display BOD value, and the biochemical reaction curve is clear at a
glance. The most ideal instrument for internal BOD determination. It can be widely used in
environmental monitoring, petrochemical, medical and health, teaching and scientific research
and other departments to monitor water quality.
II. Working principle
1B0D5Fundamental
Biochemical oxygen demand refers to the amount of dissolved oxygen consumed or
required to decompose organic substances in water through the reproduction and respiration of
aerobic microorganisms in water under specific conditions.The BOD5value in water is usually
expressed by the amount of dissolved oxygen (mg/L) consumed by the sample placed at 20°C
for 5 days, and recorded as“BOD5
2Determination principle
The stirrer is placed in the incubator, and according to the pre-selected range and
measurement range, a quantitative volume of water sample is poured into the culture flask, and
placed on the stirrer for continuous stirring. The temperature in the incubator was controlled at
Definition
Biochemical Oxygen Demand(BOD5)is defined as the consumption
of dissolved oxygen by aerobic microorganisms in water. The amount of
oxygen when the sample is placed in the incubator and the incubation
temperature is 20°C
After five days of culture, the dissolved oxygen consumed was measured
to determine the BOD value
2
20°C ± 1°C, and the water samples were incubated for five days after being kept at a constant
temperature. Sufficient dissolved oxygen must be ensured in the culture flask. The organic
matter in the sample undergoes biological oxidation, which is converted into oxides of nitrogen,
carbon and sulfur, during which the only gaseous carbon dioxide that escapes from the water
sample is absorbed by sodium hydroxide (or potassium hydroxide). Therefore, the reduction of
air pressure in the bottle is equivalent to the amount of dissolved oxygen consumed by
microorganisms. In this way, the BOD5value of the sample is proportional to the degree of air
pressure reduction in the bottle. The BOD5value can be obtained by measuring the change of
air pressure. Increasing or decreasing the amount of sample taken can increase or decrease
the pressure reduction value. This allows the operator to accurately measure a wide range of
BOD5values without complicated dilution steps. The change of air pressure in the culture flask
is detected by a semiconductor pressure sensor, and the BOD5value and biochemical reaction
curve of each sample are displayed cyclically by the LCD display.
III. Main technical indicators
1Measuring range01000 mg/Lwhen the BOD5value exceeds the measuring range,
it needs to be diluted
2Simultaneous determination of the number of samples: 6 samples or 8 samples each
time
3Accuracy: in line with the national standard "GB7488-87"
The BOD5value of the standard solution of glucose and glutamic acid is in the
range of 180 mg/L to 230 mg/L
4Display: The LCD display cyclically displays the BOD5value and biochemical reaction
curve of each sample.
5Culture temperature20±1
6Power supplyAC 220V±22V 50Hz±0.5Hz
7Power consumptionInstrument≤50W,Incubator≤300
8The instrument can save the BOD5values and biochemical reaction curves of the
eight samples analyzed last time
3
IV. Installation and use
IEnvironmental conditions for the installation of this instrument:
1Ambient temperature0℃~40℃。
2Relative humidity≤80
3There is no strong vibration and strong electromagnetic field in the surrounding
environment.
4The instrument should avoid direct exposure to strong light.
IIDescription of the functional components of the instrument
1Front panel of the instrument host
Schematic diagram of the front panel of the instrument host
0-9Numeric keys Yes/No: Operation prompt Yes/No key
Enter: Operation prompt and digital input confirmation key
Set time: press the "set time" button under the system time to modify the time;
2The top of the instrument panel
Schematic diagram of the rear panel of the instrument host
1. Power switch 2. Power socket 3. Stirrer
4
During the experiment, it drives the stirrer in the culture bottle to stir the sample solution,
so as to promote the oxygen in the air in the culture bottle to dissolve in the sample
solution.
4BOD culture bottle
The samples are put into culture flasks for biochemical culture. The culture flasks have
been specially screened and cannot be interchanged between each instrument, let alone
replaced by other similar flasks.
IIIInspection steps of the instrument system
1Check whether it is normal according to the instructions of the incubator. When the
control temperature is 20 °C, the accuracy after constant temperature should meet the
requirements of 20 °C ± 1 °C.
2Place the host in the incubator, connect one end of the power cord to the host, and plug
the other end into the incubator.
3Turn on the power of the instrument host.
4Add a small amount of tap water to any culture bottle, put a stirrer as shown in Figure 3,
and place the bottles in sequence on the corresponding position of the upper cover of
the instrument stirrer. vortex. If all the above checks are normal, the experiment can be
carried out.
V. Analysis method and analysis steps
(I)preparation of four kinds of inorganic salts (nutrient solution);
Take four cleaned volumetric flasks with a capacity of 1 liter and prepare as follows:
1Buffer
Dissolve the following reagents in distilled water and dilute to 1 liter.
121.75g dipotassium hydrogen phosphateK2HPO4
28.5g potassium dihydrogen phosphateKH2PO4
333.4g disodium hydrogen phosphate Na2HPO4·7 H2O humidity is stable at
61.07%~80.51%)
41.7g of ammonium chlorideN H4Cl
2Magnesium sulfate solution
5
Dissolve 22.5 g of magnesium sulfateMgSO 4·7H2Oin distilled water and dilute to 1
liter.
3Calcium chloride solution
Dissolve 27.5 grams of calcium chlorideCaCl2in distilled water and dilute to 1 liter.
4Ferric chloride solution
Dissolve 0.25 g of ferric chlorideFeCl3·6H2Oin distilled water and dilute to 1 liter.
5Nitrification inhibitor solution: Dissolve 500 ml of propylene thiourea in 1000 ml of
distilled water; generally, nitrification inhibitor does not need to be added to the water
sample. Add 1 ml of nitrification inhibitor solution per liter of dilution water.
IIMeasurement of actual sample BOD5
1Turn on the power supply of the incubator, so that the displayed temperature of the
incubator is 20°C (see the instruction manual of the incubator for details). Put the host
into the incubator, connect the host and the incubator with the power cord, and turn on
the power of the instrument host.
2Pre-estimate the range of the BOD5value of the sample to be tested, and select the
closest range. If it is impossible to estimate, the COD value of the sample can be
measured first, and then the BOD5value of the sample can be determined according to
the COD value of the sample (usually, the BOD5value of the sample is 0.8 times the
COD value of the sample). For samples with BOD5value below 1000mg/L and
containing enough aerobic microorganisms, no inoculation is required, and the
sampling amount can be directly obtained from the water sampling scale according to
the selected measurement range. According to the number of samples to be tested (up
to 6 samples can be measured, the instrument displays 8, and the latter two are not
used) to determine the use of several culture flasks to measure one of the samples. If
there are only two water samples, choose 2 to 4 culture bottles to measure one of the
water samples, estimate the range of the BOD5value of the water sample in advance,
determine the sampling amount of each culture bottle, and determine the required
amount of several culture bottles. total sample size. Place the water sample in a large
beaker (1000mL or 2000mL) and add 1mL of each of the four inorganic salts per liter of
6
water sample. Put the beaker into the incubator and stir on a stirrer at a constant
temperature (2-3 hours). At the same time, the pH value of the water sample must be
adjusted, which should be 6.7 to 7.5 (the optimum point is pH 7.2). If it exceeds this
range, it can be neutralized with an appropriate concentration of sodium hydroxide or
sulfuric acid. Then measure the water sample with the measuring cylinder according to
the determined sampling amount and pour it into the culture bottle. Similarly, other
water samples can be measured.
Table 1 Water sampling scale
Sample BOD5value rangemg/L
Sampling volume
mL
025
485
050
433
0100
358
0200
265
0300
211
0400
175
0600
130
0800
104
01000
86
Note: If inoculation and dilution are required, samples should be taken according to the
above table after inoculation and dilution.
3Put a stirrer in each culture bottle, and place the culture bottle on the corresponding
position of the agitator. Pay attention to the correspondence between the culture bottle
number and the channel number on the mixer panel. Generally, the shorter the
connection distance, the better, and specify the inside The bottle numbers are "2", "4",
"6", and numbers from the left, and they are located on the inside of the incubator; the
bottle numbers that are close to the plastic tube are "1", "3", "5", and numbers from the
left. , the position is outside the incubator; the order left of the 6 pressure sensors is "1",
"2", "3", "4", "5", "6", and the position is outside the incubator. Stir the test water sample
7
until the temperature of the water sample reaches 20°C ± 1°C (about 1 to 2 hours).
4Take 6 cleaned sealed cups, put solid NaOH or KOH (or 5 to 6 NaOH particles) in the
cups that account for about 1/4 of the total height, and smear the two surfaces of the
sealed cups that are in contact with the bottle mouth and the connector Apply a thin
layer of vacuum silicone grease to the mouth of each bottle. If the sealing is good, it can
be left unpainted. Tighten the cap of the bottle connected to the hose on the culture
bottle, and at the same time plug the stoppers on the 6 reference air pressure chambers
on the stirrer. During this process, do not let NaOH or KOH fall into the culture bottle.
5After 30 minutes of stability, operate the instrument host.
6After the instrument host is turned on, the display is as follows:
7The instrument will display the system settings after about 1 second
8Press 1 and press Enter to modify the system time
8
Modification method:
Press the set time key, enter the system time to be modified, such as: July 23, 2005;
8:19:00. Enter 05-07-23-08-19-00 respectively, and press the Enter key to confirm, and
press the Enter key again to return to the system setting screen. If you do not need to
modify the system time, this step can be omitted.
Note: In July, you can't just enter a 7, you should enter 07, and the system will respond.
9Press 2 and press Enter to query the experimental results. The following screen is
displayed:
This step is used to query the BOD5value and biochemical reaction curve of the last
six samples (channels 7 and 8 are random) stored in the instrument. Input the channel
number to be displayed and press Enter to confirm, the BOD value and biochemical
reaction curve of the channel will be displayed, press Enter again to return to the query
result screen, and press Enter again to return to the system setting screen. If the query
result is not required, this step can be omitted.
10Press 3 and press Enter to automatically analyze. The following screen is displayed:
This sentence means that if the instrument fails to analyze continuously for some
short-term reason, if it has been analyzed for 30 hours, such as continuous analysis
Continue last interrupted analysis?
(Yes/No)
9
from 30 hours after restarting, select Yes, then only after another 90 hours of analysis
can be achieved. 120 hours of five-day analysis.
If you select No, the instrument will wait for about 10 seconds to display as follows: 1,
5 days of biochemical culture; 2, 10 days of biochemical culture; input 1, start 5 days of
biochemical culture; input 2, start 10 days of biochemical culture. At the same time, the
instrument enters the next screen.
Coefficient: Please select the channel number (1-8; the 7th and 8th channels are not
used), if you do not need to modify the coefficient of each channel, please press the
Enter key to enter the next screen. If you need to modify the coefficient, please enter
the channel number, enter the coefficient to be modified, and press the Enter key after
all channels have been modified. The so-called coefficient is the actual result of each
channel multiplied by the coefficient to get the displayed result.
When the modification is completed, press the Enter key to enter the next screen:
Enter the channel number to be modified (channels 7 and 8 are not used), such as 1,
after pressing the Enter key, the display is as follows:
10
Select the appropriate range, for example, press 4, then press the Enter key, the
instrument displays
After about two seconds of display, the instrument returns to the previous screen. The
default range of the instrument is 0-100mg/L. After each channel is set, please press the
Enter key to enter the next screen. The instrument starts from 0 hours, after 120 (or 240
hours of analysis. At this time, the instrument enters to display the BOD value and
biochemical reaction curve of each channel, and displays the current system time and
system running time at the same time, and the instrument displays the BOD of a channel
every minute. Values and biochemical reaction curves are printed every half hour.
11
After the analysis of the instrument is completed, the values of 8 channels are displayed in
a circular manner, waiting for the operator to shut down.
IIIMeasurement data processing:
1For undiluted samples, simply read the reading displayed on the instrument to get the
sample BOD value.
2For the samples that have been diluted and inoculated, the readings on the display can
be read out, and then calculated according to the following formula:
Sample BOD5reading-Inoculum BOD5reading×Inoculum %
Sample actual BOD5
×Dilution factor
Sample liquid%
Example 1. There is a sewage sample whose BOD5 value is estimated to exceed
1000mg/L, so dilution pretreatment is done (no need to add inoculum). Select the range
from 0 to 600 mg/L, and the display reads 550 after five days of culture.
The actual BOD5value of the samplemg/L=550×21100mg/L
Example 2. There is an industrial wastewater sample, the microorganisms are insufficient
to inoculate, and the BOD5value is about 60mg/L. The inoculation is carried out with
domestic sewage, and the inoculation amount is 10% (that is, 90 samples to 10 inoculum
solutions). The estimated BOD5value of the inoculum It is about 30mg/L, and the
industrial wastewater is in the range of 0-100mg/L during the experiment.
The inoculum of the parallel sample test was selected from the range of 0-50 mg/L
(sampling amount was specified in the respective range). After five days of incubation, the
12
display readings were 71.4 and 42.3, respectively.
Sample actual BOD5valuemg/L)=
%90 %103.424.71
74.6mg/L
Example 3. There is an industrial wastewater that is poisonous, and the estimated BOD5
value is about 700mg/L. Before the measurement, the sample was diluted 10 times and
inoculated with living water. The BOD5value of the inoculum was about 60mg/L, and the
inoculation amount was 10% ( 9 diluted samples, 1 inoculum), treated industrial
wastewater and inoculum were all sampled in the range of 0-100 mg/L. After five days of
culture, the numbers were 52.0 and 61.7, respectively.
Sample actual BOD5valuemg/L)=
×10509mg/L
IVBOD5test method for standard samples
In order to check the performance of the instrument, the standard sample of
glucose-glutamic acid can be used for BOD5test. Operators should be able to use the
instrument and chemical dilution operations correctly. The BOD5test method of
glucose-glutamic acid standard sample is as follows:
1Prepare dilution water
Take a 2000mL beaker, measure 2000mL of distilled water with a measuring cylinder and
pour it into the beaker, and add 2mL of each of the four inorganic salts to the beaker,
which is the dilution water.
2Dissolve 300mg of glucoseC6H1206and 300mg of glutamic acid in 2 liters of dilution
water (such as laboratory glucose with a crystal water, glucose needs to be weighed
330mg, this standard solution should be freshly prepared before each use). Put a stirrer
in the beaker, and place the beaker on the amplifier in the incubator to stir at a constant
temperature for 2 to 3 hours.
3Use a 1000mL beaker to take fresh domestic sewage as the inoculum, put the beaker
on the stirrer in the incubator and keep the standard sample constant for 2-3 hours at
the same time.
13
Figure 2 The water sample is poured into the culture bottle
Figure 3 The stirrer is put into the culture bottle
14
Figure 4 Figure 4 Put the CO2absorbent KOH or NaOH in the sealed cup
4After the standard sample is completely dissolved, pour out 200mL from the graduated
cylinder, and then take 200mL of domestic sewage from the graduated cylinder and
pour it into the standard sample. The standard sample after inoculation is still placed on
the stirrer in the incubator and stirred at a constant temperature for 1 to 2 hours.
5Measure the standard sample after inoculation according to the sampling amount
specified in the measurement range of 0-300mg/L in the table of instructions, pour it into
8 culture bottles respectively, and then perform the measurement according to steps
3-10 of the actual sample measurement mentioned above.
If the BOD5value is in the range of 180mg/L230mg/L, it indicates that the method
used by the instrument is suitable and the result is correct. If the measurement result
deviates from the above range, it is necessary to check whether the performance and
operation of the instrument and the inoculation water meet the requirements (see
"Evaluation of measurement results").
VFactors Affecting BOD5
1Determination
Dissolved oxygen
The samples taken in winter are supersaturated with dissolved oxygen because the
test temperature is set at 20 °C, and the samples taken in summer may be
under-saturated with dissolved oxygen at 20 °C. These samples should be stirred and
aerated prior to BOD5determination in order to adjust the dissolved oxygen to around
the 20°C saturation point.
2pH
The pH value of the test water sample should be adjusted to 6.7 to 7.5 (the optimum
point is pH 7.2). The decrease in BOD5reading may be due to the pH value of the
sample being tested exceeds this range. For samples containing a large amount of
acid or alkali, the BOD5reading may be will be lower than the actual content.
Acidic or alkaline water samples should be neutralized with appropriate concentrations
of NaOH or H2S04.
15
If the industrial wastewater contains acid or salt oxides, or requires high dilution, for
the standard five-day BOD5determination, pH 7.2 phosphate buffer can be used as
the diluent.
3Temperature
The stirrer was placed in an incubator at 20 °C ± 1 °C during the experiment. The
determination of BOD can also exceed this temperature range. For example, at 35°C or
37°C, the time required to measure BOD can be shortened to 2.5 days or 34 hours,
respectively, and the measurement results are similar to 20°C for five days. The BOD
value obtained by increasing the temperature has a good correlation with the results
measured at 20on the fifth day.
If the sample temperature exceeds 20°C when sampling, or the sample temperature is
less than 20°C, the sample can be kept in an incubator for constant temperature. The
sample is required to be processed prior to sample measurement.
4Dilution
The measuring range of the instrument is 01000mg/L. If the estimated BOD5value of
the test sample is higher than 1000mg/L, the sample can be diluted with dilution water.
The added dilution water should also be kept at 20°C, and aeration should be used to
saturate the oxygen. If several identical samples are required to be tested, a sufficient
amount of the original water sample should be diluted, and the volume corresponding to
the measuring range should be taken from the diluted sample. . For example, when the
original water sample is diluted twice, the dilution factor is 2; when the original water
sample is diluted by 1:10, the dilution factor is 10.
5Inoculate
Inoculation solution
The solution used for inoculation is the supernatant of untreated fresh
domestic sewage placed at 20°C for 24-36 hours.
In the next experiment, if you want to use the previously measured water
sample as the inoculum, it should be filtered through filter paper. This filtrate should
be stored under refrigeration (about 20 °C) and protected from light. Generally, it
may be effective within two months.
16
6Inoculation method
Prepare inoculation solution
Put the sample to be assayed into a culture flask, and use a pipette to add 2 to 5 drops of
inoculum to the sample (depending on the sample size). Follow the steps to measure
BOD5, and the readings obtained after five days can be used as the true BOD5value of
the test sample.
NOTE: When inoculating using the above method. It is not necessary to correct
inoculated BOD5readings. Because the amount of inoculum added is too small relative to the
amount of water sample, it will not affect the BOD5reading. If the above methods fail to induce
biodegradation of organic matter in the water sample, the amount of inoculum added can be
increased. If the BOD5reading is affected by the addition of the inoculum, the inoculum and the
sample can be tested simultaneously for parallel sample determination. The amount of
inoculation is often 1%, 5%, and 10%.
VI. Normal maintenance and troubleshooting of common
faults
IThe instrument should be placed in a ventilated place, without strong electromagnetic
field interference, without direct exposure to strong light, and without major power
fluctuations. It is best that the laboratory can be equipped with a regulated power
supply and has a good grounding wire.
IIOpen all the instrument packing boxes, put the host into the incubator, and connect
them with special cables.
IIICleaning work after the experiment
What is vaccination
The BOD5 test requires that the water sample contains organic
matter for biological oxidation and an appropriate amount of aerobic
bacteria that oxidize organic matter, as well as other microorganisms that
devour organic matter and promote the growth of aerobic bacteria. If there
is no or almost no such microorganisms in the water sample, a certain
proportion of such microorganisms must be added to the water sample. This
process should be called inoculation.
17
After completing the measurement, follow the steps below to clean
1Culture bottle
Rinse the culture bottle with hot water several times, wash away the deposits on the
inner wall of the bottle with hot soapy water and a brush, and rinse with clean water
several times.
2Stirrer
Wash the experimental stir bar with detergent solution and rinse.
3Sealed cup
Wipe off applied vacuum silicone ester, wash off residue and CO2 absorber with wash
solution, rinse well and dry.
Note: The inner surface of the culture bottle stopper is often stained with sealing oil.
The inner surface must be wiped clean, and the vacuum silicone grease at the contact
between the connector and the sealing cup must be wiped off.
IVTroubleshooting of common faults
BOD5readings gradually increased during a five-day incubation period at 20°C ± 1°C.
(However, the increments between each day will be smaller and smaller over time).
The biochemical reaction curve (BOD5-time curve) will be similar to curve A shown in
the figure below. If similar curves cannot be obtained, the influencing factors can be
determined according to the following checklist.
Checklist
18
Result
Possible reason
Take measures
Reading drops
Air leak
Check whether the sealing cup
is in good condition, whether the cap
of the sealed culture bottle and the
sealing bolt are tightened, and
whether various impurities and
residues on the cap are removed.
Check the plastic pipes for cracks,
aging and deformation. When this
happens, a new tube should be
replaced, and attention should be
paid to the material length and inner
diameter of the original tube.
Result
Possible reason
Take measures
The instrument does not
respond
CO2absorbent
leaked, pH
changed, and air
leakage was
serious.
The range
selection is too
large, resulting
in interference
gas and so on.
Avoid putting too much absorbent
into the bottle as it will swell due to
absorbing CO2.
Find the leak point, mainly
check the pipeline connection.
Select the appropriate range.
This phenomenon may occur
due to many factors caused by the
sample. The influencing factors are
determined, and appropriate
pretreatment work is carried out
before the measurement.
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Huazheng HZJY880 Operating instructions

Type
Operating instructions

Huazheng HZJY880 Computer BOD5 Measator is a reliable instrument for measuring Biochemical Oxygen Demand (BOD5), a crucial indicator of water quality. With its advanced features, it offers precise and efficient BOD5 determination for various applications. Here are some of its capabilities:

  • Accurate Measurement: Provides accurate BOD5 values comparable to the chemical dilution method, ensuring reliable results.

  • Real-Time Monitoring: Continuously monitors BOD5 levels throughout the incubation period, allowing for real-time observation of the biochemical reaction curve.

  • Wide Measurement Range: Covers a wide measurement range of 0 to 1000 mg/L, accommodating diverse water samples. For values exceeding this range, simple dilution is recommended.

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